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(Reaffirmed 2003)
IS 10447 - 1983
UDC 628.544 (026) : 669.18.013.5
© Copyright 1983
INDIAN STANDARDS INSTITUTION
MANAK BHAVAN. 9 BAHADUR SHAH ZAFAR MARG
NEW DELHI 110002
Gr 3
April 1983
iIndian Standard
GUIDELINES FOR UTILIZATION AND DISPOSAL OF SOLID WASTES FROM INTEGRATED STEEL PLANTS
Chairman | Representing |
---|---|
SHRI A. D. BHIDE | National Environmental Engineering Research Institute, Nagpur |
Members | |
SHRI A. V. SHEKHDAR (Alternate to Shri A. D. Bhide) | |
DR A. ALAM | Indian Council of Agricultural Research, New Delhi |
SHRI S. C. ANAND | Rajasthan State Agro Industries Corporation Ltd, Jaipur |
SHRI R. K. SURI (Alternate) | |
SHRI P. K. BANERJEE CHOWDHURY | The Corporation of Calcutta, Calcutta |
SHRI P. K. CHAKRAVARTY | The Tata Iron and Steel Co Ltd, Jamshedpur |
CHIEF ENGINEER (THERMAL DESIGN) | Central Electricity Authority, New Delhi |
DR S. K. CHOPRA | Cement Research Institute of India, New Delhi |
DR K. C. NARANG (Alternate I) | |
DR S. C. AHLUWALLIA (Alternate II) | |
SHRI DALJIT SINGH | Steel Authority of India Ltd, New Delhi |
SHRI J. C. SEHGAL (Alternate) | |
DIRECTOR (SOLID WASTE MANAGEMENT) | Municipal Corporation of Greater Bombay, Bombay |
DEPUTY CITY ENGINEER (Alternate) | |
SHRI A. H. GANDHI | Municipal Corporation, Ahmadabad |
SHRI JWALA PRASAD | Ministry of Agriculture, New Delhi |
SHRI D. N. KHURANA | Municipal Corporation of Delhi, Delhi |
SHRI R. K. KASHYAP (Alternate) | |
SHRI S. M. MAHMOOD | Triveni Structurals Ltd, Allahabad |
SHRI S. G.JAIN (Alternate) | |
SHRI H. C. NANDI | Central Fuel Research Institute (CSIR), Dhanbad |
SHRI M. PARABRAHMAN | Department of Environment, Government of India, New Delhi |
© Copyright 1983 INDIAN STANDARDS INSTITUTION This publication is protected under the Indian Copyright Act (XIV of 1957) and reproduction in whole or in part by any means except with written permission of the publisher shall be deemed to be an infringement of copyright under the said Act. |
Chairman | Representing |
---|---|
SHRI P. SAHA | Calcutta Metropolitan Development Authority, Calcutta |
SHRI S. SUBBA RAO | All India Institute of Hygiene and Public Health, Calcutta |
SHRI A. V. RAO (Alternate) | |
DR D. C. TAPADAR | Indian Paper Mills Association, Calcutta |
DR N. D. MISRA (Alternate) | |
SHRI J. M. TULI | Engineers India Ltd, New Delhi |
SHRI A. D. JALGAONKAR (Alternate) | |
SHRI S. VENKATARAMAN | King Institute, Madras |
DR C. VENKOBACHAR | Indian Institute of Technology, Kanpur |
DR A. V. S. PRABHAKARA RAO (Alternate) | |
SHRI S. K. MATHUR, | Director General, ISI (Ex-officio Member) |
Head (Chem) |
Secretary
SHRI A. K. BAHL
Assistant Director (Chem), ISI
Members | |
SHRI H. S. ASWATH | Bokaro Steel Limited, Bokaro |
SHRI SHIV KUMAR (Alternate) | |
SHRI N. R. HILLOOWALLA | The Associated Cement Companies Ltd, Bombay |
SHRI J. V. JOSHI (Alternate) | |
SHRI V. K. JAIN | Central Building Research Institute (CSIR), Roorkee |
SHRI DINESH CHANDRA (Alternate) | |
SHRI U. S. B. KINI | Bhilai Steel Plant, Bhilai |
SHRI D. SUBRAHMANYAM (Alternate) | |
SHRI Y. R. PHULL | Central Road Research Institute (CSIR), New Delhi |
SHRI S. K. TITUS | National Environmental Engineering Research Institute, Nagpur |
SHRI R. S. DHANESHWAR (Alternate) |
Indian Standard
GUIDELINES FOR UTILIZATION AND
DISPOSAL OF SOLID WASTES FROM
INTEGRATED STEEL PLANTS
This Indian Standard was adopted by the Indian Standards Institution on 28 February 1983, after the draft finalized by the Solid Wastes Sectional Committee had been approved by the Chemical Division Council.
In any industry when basic raw materials are processed, along with the main products some other materials are also produced. Depending on the characteristics of these materials some of them, called by-products, may be economically used either in the same industry or in another industry, whereas the rest, called wastes, are totally discarded.
An Indian integrated iron and steel plant produces approximately 1.1 tonne of solid wastes for every tonne of ingot steel produced. This figure does not include ore fines and slimes of ore crushing plant at mines, and middlings or rejects at a coal washery.
Dumping sites of the solid wastes preferred for recycle should be located adjacent to the recycle process units. For example, solid wastes which are to be recycled to sintering plant should be dumped in close proximity to the sintering plant for effective recycling.
This standard prescribes guidelines for the present and possible future uses of the solid wastes generated in an integrated steel plant. Amount of generation and characteristics of these wastes have also been given.
This standard does not cover wastes generated at mines and collieries. It also does not include spillage at various stages of processing which is recycled into the system, for example, dust at coke ovens, sinter plant, etc, and also wastes generated in small quantities like dust from open hearth furnaces and sludge from water softening plants.
3Blast Furnace Gas Cleaning Plant Sludge—These are finer particles of dust finally removed from the blast furnace gas in the gas cleaning plant.
Blast Furnace Slag—This is the waste material, consisting mainly of CaO, SiO2, Al2O3 and MgO, coming out of the iron making blast furnaces. It is originally in liquid form but is finally disposed off as a solid after cooling.
Bottom Ash—The coal used in the grate type boilers, after combustion, turns into clinker form which is known as bottom ash.
Coal Tar Sludge—This material collects below the tar in the coke ovens by-product plant. It is a soft solid mass which turns into fluid at a temperature around 75-80°C.
Fines and Dust from. Calcining Plant—These fines are generated during the processing of dolomite for the supply of sized material to steel melting shops. Lime and dolo dust are also generated during calcination of lime stone and dolomite in the kilns.
Flue Dust—The gas emitted by a blast furnace is laden with dust as it comes out of the furnace. During the gas cleaning process, the coarser particles, collected in the dust catcher, are called flue dust.
Fly Ash—Fly ash is a finely divided residue resulting from the combustion of ground of powdered coal and carried along with the flue gases of boilers fired by pulverized coal.
Foundry Wastes
Mill Scale—While steel ingots or other sections are heated in soaking pits or reheating furnaces before rolling, the outer skin of the material is oxidised. The oxidised layer, called mill scale, drops down in the furnaces or under the rolling table.
Slimes—During crushing and washing of iron ore within the steel plant for improving its quality and size, finer fraction (less than 200 µm) is carried away by water in the form of slurry into a pond. These fine particles of iron ore are called slimes.
LD Converter/Open Hearth Slag—This material is generated during conversion of iron into steel in a steel making furnace.
4Wastes from Refractories—Used broken bricks are generated during breaking of the refractory lining for rebuilding various furnaces.
Dusts of various refractory materials are produced during the manufacture of refractory mortars or bricks in integrated steel plants.
The characteristics, quantity, and possible uses of the various solid wastes generated in an integrated steel plant are given in Table 1.
5SL NO. | TYPE OF WASTE | TYPICAL GENERATION FOR INTEGRATED STEEL PLANT OF 2 MILLION TONNE INGOT STEEL | PERCENT OF TOTAL QUANTITY | TYPICAL CHEMICAL ANALYSIS PERCENT (AND SIZE) | MODE OF UTILIZATION/DISPOSAL | |
---|---|---|---|---|---|---|
(1) | (2) | (3) | (4) | (5) | (6) | |
i) | Iron ore slimes from ore crushing plant inside works* | tonne/month 2 500 - 3 500 (4-6 percent of ore processed) |
1.7 | Fe = 55-60, SiO2 = 3-6 Al2O3 = 4-7 (60 percent smaller than 75 µm) | As a feed to pelletizing mix (20 percent Max) for improving Al2O3/SiO2 ratio of burden and improved strength of pellets during reduction. | |
ii) | Blast furnace flue-dust* | 5 000 - 6 000 (35-45 kg/t hot metal) | 3.2 | Fe = 32-35, SiO2 = 7-9 Al2O3 = 6-7, MgO = 3-4 C = 21-24 (80-90 percent between 500 and 75 µm) | As a feed to the sinter plant. Ratio to be decided on the basis of operating condition of plant and size of flue dust. | |
iii) | Sludge from gas cleaning plant | 3 500-4500 (25-30 kg/t hot metal) | 2.3 | Fe = 33-35, SiO2 = 6-8 than 80 percent smaller than 45 µm) | Generally disposed off on land in the form of cakes. | |
iv) | Blast furnace slag† | 85 000 - 95 000 (600 kg/t hot metal) | 52.2 | CaO = 31-33, SiO2 = 30-33, Al2O3 = 22-24, MgO =9-12 | a) Granulated to make slag cement, b) To make light weight slag for use as insulating material, and c) Air cooled slag boulders for building roads.6 |
|
v) | Steel making slag† | |||||
a) Open hearth slag (30/40 scrap, 60/70 hot metal) | 27 000 - 30 000 | 16.6 | Flush slag =SiO2 = 20.1, Fe2O3 = 3.6, FeO = 30.4, Al2O3 = 5.9, CaO = 20.2, MgO= 6.1, P2O5 = 4.6, MnO = 7.0 | a) High CaO/SiO2 ratio slag as a soil conditioner in agricultural fields having acidic soil. | ||
Tap slag SiO2 = 18.6, Fe2O3 = 4.0, FeO = 13.1, Al2O3 = 4.8, CaO = 37.0, MgO = 12.0, P2O5 = 3.3, MnO = 7.0 | b)Partly charging to the sinter mix, and c)High P2O5 slag for manufacture of fertilisers. |
|||||
b) LD converter slag† | 120 - 220 kg/t steel | CaO = 43-50 SiO2 = 13-16, MgO = 5-8, MnO = 3-5, P2O5 = 2-3, FeO = 16-20 | a) Soil conditioner for acidic soil, and b) Source of flux in the blast furnace either directly or through the sinter. |
|||
vi) | Mill scale (Both primary and finishing mills)* | 6 000 - 7 000 (2.5 - 3.5) 3.5percent of input material rolled | Fe = 31.2, FeO = 63.3 SiO2 = 1.4, Al2O3 = 0.4, CaO = 0.2, MgO = 0.9 | a) As a feed in the sinter plant (—10 mm), b) Recycle through open hearth furnace (+6 mm), |
||
c) Feed to pelletizing mix (up to 5 per-cent) to increase compressive strength of pellets, and | ||||||
d) As feed to blast furnace (+ 10 mm). | ||||||
vii) | Fines and dust at calcining plant | 1.1 | ||||
a) Dolo fines (—5 mm)* | 1 300 - 1 400 | — | As a feed in sinter. | |||
b) Dolo dust* | 100-150 | — | As a feed in sinter. | |||
c) Lime dust† | 400 - 450 | — | a) For spreading on the ground with tar sludge for preventing growth of vegetation, and b) Adding to steel melting shops after bri-quetting.7 |
|||
viii) | Refractories | 0.5 | ||||
a) Used broken bricks† | 400 - 500 | — | Crushed and used for making mortar. | |||
b) Dust (chrome, magnesite, kyanite, clay, etc)† | 200-250 | — | Used for making mortar. | |||
c) Dust (magnesite)* | 100-150 | — | Feed to sinter mix. | |||
ix) | Coal tar sludge† | 200 - 300 | — | Mixing with lime dust and hot pitching to prevent growth of vegetation. | ||
x) | Bottom ash† | 24 000 | 13.9 | SiO2 = 41.9, Al2O3 = 21.3, Fe2O3 = 5.7, CaO = 1.7, MgO = 0.94 0-94, (Na2O + K2O) = 0.32 TiO2 = 2, P2O5 = 1 Total (SO3 + SO4) = 0.54, Loss on ignition = 27.6 |
Bricks for building purposes and construction of walls by casting along with fly ash. | |
xi) | Fly ash† | 7 500 (If only coal is used) | 4.3 | SiO2 = 50.55, Al2O3 = 22.25, Fe2O3 = 2.4, CaO = <2.5, MgO = 0.25, Total (SO3 + SO4) = 2.5 (Na2O + K2O = 1.0, Max, TiO2 = 1.9. P2O5 = 0.9, Loss on ignition = 3 percent Size: more than 106 µm = 12.20 percent. 106 to 75 µm = 15.25 percent, less than 75 µm = 60-70 percent |
See IS : 10153 - 1982‡8 | |
xii) | Foundry sand* | 500 - 700 | 0.3 | SiO2 = 80 percent, balance Fe2O3, TiO2 and Al2O3 | Half of the sand may be used for recycle after screening the fused material. | |
xiii) | Sinterning plant slime (recovered from battery cyclones of exhausters and Other de-dusting units)* | 50 - 80 kg/t of sinter | — | Total Fe = 35-40, FeO = 2-4.5 SiO2 = 6.9, Al2O3 = 4-5.5, CaO = 11.14, MgO = 2.4, Loss on ignition = 7-10 percent size:0.0 percent larger than 5 mm, 0.3 percent larger than 3 mm, 50-60 percent larger than 150 µm, and 40-50 percent smaller than 150 µm. |
60 to 70 percent of the total slime may be used along with the sinter mix. All of it may be used in the sintering mix if the moisture is brought down to 10-15 percent. | |
xiv) | LD converter dust | 10 - 15 kg/t steel | — | Fe total = 65.0 (Fe metal = 24.6, FeO = 49.4 and Fe2O3 = 1) CaO = 5.7, SiO2 = 3.5, Al2O3 = 0.5, MgO = 0.9, MnO = 2.0, S = 0.14. P2O5 = 0.5 | May be used as a source of iron in blast furnace either through sinter after air classification to use + 0.125 mm (which is about 50 percent) or by briquetting with suitable binders. |
Note—The figures given are likely to vary from plant to plant depending on the raw materials used and operating conditions. Since the possible uses of wastes are dependent on their chemical and physical properties, corresponding variations are likely in this respect also.
*Suitable for re-cycling.
†Suitable for by-product recovery.
‡Guidelines for utilization and disposal of fly ash.
Base Units | |||
Quantity | Unit | Symbol | |
Length | metre | m | |
Mass | kilogram | kg | |
Time | second | s | |
Electric current | ampere | A | |
Thermodynamic temperature | kelvin | K | |
Luminous intensity | candela | cd | |
Amount of substance | mole | mol | |
Supplementary Units | |||
Quantity | Unit | Symbol | |
Plane angle | radian | rad | |
Solid angle | steradian | sr | |
Derived Units | |||
Quantity | Unit | Symbol | Definition |
Force | newton | N | 1 N = 1 kg.m/s2 |
Energy | joule | J | 1 J = 1 N.m |
Power | watt | W | 1 W = 1 J/s |
Flux | weber | Wb | 1 Wb = 1 V.s |
Flux density | testa | T | 1 T = 1 Wb/m2 |
Frequency | hertz | Hz | 1 Hz = 1 c/s (S-1 |
Electric conductance | siemens | S | 1 S = 1 A/V |
Electromotive force | volt | V | 1 V = 1 W/A |
Pressure, stress | pascal | Pa | 1 Pa = 1 N/m2 |